Phosphorus Interactions with Iron in Undisturbed and Disturbed Arctic Tundra Ecosystems.

• Published in: Environmental Science & Technology
• Main Authors: Berens, Matthew John, Michaud, Alexander Bryce, VanderJeugdt, Erin, Miah, Imtiaz, Sutor, Frederick W, Emerson, David, Bowden, William B, Kinsman-Costello, Lauren, Weintraub, Michael N, Herndon, Elizabeth M
• Format: Article in Journal/Newspaper
• Language: English
• Published: American Chemical Society 2024
• Subjects: Fe redox cycling; X-ray absorption spectroscopy; biogenic Fe mats; phosphorus; soil disturbance; tundra soils; Thermokarst; Tundra
• Online Access: https://doi.org/10.1021/acs.est.3c09072; https://pubmed.ncbi.nlm.nih.gov/38889135; https://www.ncbi.nlm.nih.gov/pmc/articles/PMC11223478/

Phosphorus (P) limitation often constrains biological processes in Arctic tundra ecosystems. Although adsorption to soil minerals may limit P bioavailability and export from soils into aquatic systems, the contribution of mineral phases to P retention in Arctic tundra is poorly understood. Our objective was to use X-ray absorption spectroscopy to characterize P speciation and associations with soil minerals along hillslope toposequences and in undisturbed and disturbed low-lying wet sedge tundra on the North Slope, AK. Biogenic mats comprised of short-range ordered iron (Fe) oxyhydroxides were prevalent in undisturbed wet sedge meadows. Upland soils and pond sediments impacted by gravel mining or thermokarst lacked biogenic Fe mats and were comparatively iron poor. Phosphorus was primarily contained in organic compounds in hillslope soils but associated with Fe(III) oxyhydroxides in undisturbed wet sedge meadows and calcium (Ca) in disturbed pond sediments. We infer that phosphate mobilized through organic decomposition binds to Fe(III) oxyhydroxides in wet sedge, but these associations are disrupted by physical disturbance that removes Fe mats. Increasing disturbances of the Arctic tundra may continue to alter the mineralogical composition of soils at terrestrial-aquatic interfaces and binding mechanisms that could inhibit or promote transport of bioavailable P from soils to aquatic ecosystems.